Method and apparatus for treatment of a fluid stream

ABSTRACT

A method for treating a fluid by providing a raw fluid to a process tank. The raw fluid may be water having varying degrees of contamination or another type of fluid. The method further consists of adding an ion exchange resin to the process tank to form a raw fluid/ion exchange resin mixture. After the fluid has been sufficiently contacted with the ion exchange resin, treated fluid is removed from the process tank through a membrane filter located within the process tank. The method is completed by regenerating the ion exchange resin within the same process tank.

RELATED APPLICATION DATA

This application is a continuation of U.S. patent application Ser. No.11/208,905, filed Aug. 22, 2005, now U.S. Pat. No. 7,144,510, issuedDec. 5, 2006, entitled METHOD AND APPARATUS FOR TREATMENT OF A FLUIDSTREAM, which application is a continuation of commonly assigned U.S.patent application Ser. No. 10/727,441, filed Dec. 3, 2003, now U.S.Pat. No. 7,025,884, issued Apr. 11, 2006, entitled METHOD AND APPARATUSFOR TREATMENT OF A FLUID STREAM, which application is acontinuation-in-part of commonly assigned U.S. patent application Ser.No. 09/991,478, filed Nov. 9, 2001, now U.S. Pat. No. 6,783,681, issuedAug. 31, 2004, entitled METHOD AND APPARATUS FOR TREATMENT OF DRINKINGWATER, which application claims benefit of U.S. Provisional PatentApplication Ser. No. 60/247,124, filed Nov. 10, 2000, entitled METHODAND APPARATUS FOR DRINKING WATER TREATMENT; all of said applications areincorporated herein by reference in their entirety.

TECHNICAL FIELD

The present invention is directed to a method and apparatus for thetreatment of a fluid stream, and more particularly to a treatmentprocess utilizing a regeneratable ion-exchange resin in combination withan immersed membrane filter in a single process tank.

BACKGROUND ART

Treatment and purification of raw water in order to make it suitable fordrinking or the treatment of an industrial fluid stream which may bewater can be accomplished by a number of methods. The character of agiven water stream may lend itself to the use of a particular treatment.Ion-exchange resins are used in water treatment systems in order toremove dissolved compounds, some of which are organic. Microfiltrationand Ultrafiltration membranes are used to remove particulates. For awater stream that contains both these components, one treatment must beused, followed by the second. The need for two separate steps istime-consuming, requires additional equipment, and increases the overallcost of the treatment system. Accordingly, there remains a need for animproved water treatment system that can remove particulates anddissolved organic compounds and which is cost- and time-effectivecompared to present systems.

Benedek, U.S. Pat. No. 6,027,649, discloses the treatment of drinkingwater in a single reactor tank using a ZEWEED® submerged membrane filterin conjunction with a flocculent mixed in the reactor tank andmaintained in suspension by use of an air bubbler. The flocculent isintended to remove organics, color, bacteria, cysts and otherimpurities. Use of the flocculent taught by Benedek requires maintainingpH in a range from 5-9. This may require addition of acids or bases to araw water supply to maintain the necessary pH range. While Benedekteaches a single tank using a flocculent in combination with a membranefilter, use of the flocculent for organic removal requires subsequentdisposal of the spent flocculent. Thus, not only must suitable disposalfor the spent flocculent be arranged, new coagulants must be provided tothe reactor tank to form the necessary flocculent. Benedek alsodiscusses the desirability of adding activated carbon to the reactortank for the removal of dissolved organics. However, as with theflocculent, this creates disposal problems for spent activated carbonand requires replenishment of the reactor tank with new activatedcarbon.

Daly, U.S. Pat. No. 6,120,688, is directed to a water purificationmethod also utilizing a ZEWEED® membrane filter. More particularly, Dalyteaches initial particulate removal using the ZEWEED® filter followed byapplication of reverse osmosis to the filtered water. While Dalyeliminates the disposal problems associated with the flocculent andactivated carbon of the Benedek patent, the Daly patent requires a twostep treatment process which increases plant size and cost requirements.

The present invention is directed to overcoming one or more of theproblems discussed above.

SUMMARY OF THE INVENTION

A method for treating a fluid by providing a raw fluid to a processtank. The raw fluid may be water having varying degrees of contaminationor another type of fluid. The method further consists of adding an ionexchange resin to the process tank to form a raw fluid/ion exchangeresin mixture. After the fluid has been sufficiently contacted with theion exchange resin, treated fluid is removed from the process tankthrough a membrane filter located within the process tank. The method iscompleted by regenerating the ion exchange resin within the same processtank.

The method may further consist of agitating the raw water/ion exchangeresin mixture sufficiently to maintain the ion exchange resin insuspension. In addition, the method may consist of reusing or recyclingthe regenerant through multiple regeneration steps. In addition, theregenerant may be periodically filtered to restore its regenerativeproperties. The ion exchange resin may be a magnetic ion exchange resin.

An alternative embodiment of the invention consists of providing rawfluid to a process tank and adding a magnetic ion exchange resin to theprocess tank to form a raw fluid/magnetic ion exchange resin mixture.Thereupon, treated fluid is removed from the process tank through amembrane filter located within the process tank. The method of thealternative embodiment is completed by separating the magnetic ionexchange resin from the raw fluid/magnetic ion exchange resin mixtureusing a magnetic separator. The magnetic ion exchange resin may beregenerated in an external column or within the process tank and, ifregenerated externally, the regenerated magnetic ion exchange resin maybe returned to the process tank. The regenerant may be recycled for usein multiple regeneration steps and periodically filtered to restore itsregenerative properties.

Another alternative embodiment consists of providing an upflow bedcontaining ion exchange resin within a portion of a process tank,flowing a stream of fluid through the upflow bed, and removing treatedfluid from the process tank through a membrane filter located within theprocess tank. This alternative embodiment of the method is completed byregenerating the ion exchange resin in the upflow bed portion of theprocess tank. The regenerant may be recycled for use in multipleregeneration steps and periodically filtered to restore its regenerativeproperties. Alternatively, the upflow bed containing the ion exchangeresin may be maintained in a separate container, apart from but in fluidcommunication with the process tank.

Another alternative embodiment consists of a method of treating a fluidby providing raw fluid to a process tank, adding an ion exchange resinto the process tank to form a mixture, and removing treated fluid fromthe process tank through a membrane filter located within the processtank. This alternative method further consists of regenerating the ionexchange resin with a regenerant in a regeneration step, recycling theregenerant for use to regenerate the ion exchange resin in multipleregeneration steps, and recovering a portion of the spent regenerant bymembrane separation of the regenerant and contaminants.

A further alternative embodiment is a method of regenerating an ionexchange resin consisting of removing treated fluid from a process tankwhile retaining a substantial portion of the ion exchange resin withinthe process tank, adding regenerant to the process tank, mixing theresin and the regenerant, and removing the regenerant from the processtank while retaining a portion of the ion exchange resin within theprocess tank. The retained resin may be rinsed within the process tankafter removing the regenerant. A second, make up portion of ion exchangeresin may be added to the process tank to make up for ion exchange resinlost to the system.

BRIEF DESCRIPTION OF THE DRAWINGS

FIG. 1 is a schematic of the drinking water treatment system accordingto the present invention.

FIG. 2 is a simplified schematic of an embodiment of the presentinvention wherein regeneration of the resin is accomplished by acountercurrent column.

FIG. 3 is a simplified schematic of an embodiment of the presentinvention wherein regeneration of the resin is accomplished in theprocess tank.

FIG. 4 is a schematic showing a basic water treatment process.

FIG. 5 is a schematic showing the membrane/resin process of the presentinvention.

FIG. 6A is a graph showing the Effect of Controlling the Contactor ResinConcentration on the Bed Volumes Treated at Regeneration, applying amathematical model to the proposed process as depicted in FIG. 1.

FIG. 6B is a graph showing the Effect of Controlling the ContactorHydraulic Residence Time on the resin contact Time at Regeneration,applying the mathematical model to the proposed process as depicted inFIG. 1.

FIG. 6C is a graph showing the Effect of Controlling Resin Recycle onthe Bed Volumes Treated at Regeneration, applying the mathematical modelto the proposed process as depicted in FIG. 1.

FIG. 7 is a schematic of a fully realized water treatment systemaccording to the present invention.

FIG. 8 is a simplified schematic of an embodiment of the presentinvention wherein regenerant is recycled and recovered.

FIG. 9 is a simplified schematic of an embodiment of the presentinvention suitable for continuous operation where magnetic ion exchangeresin is used with regenerant recycling and recovery.

FIG. 10 is a simplified schematic of an embodiment of the presentinvention showing an upflow bed within a chamber of the process tank.

FIG. 11 is a simplified schematic of an embodiment of the presentinvention showing a separate upflow bed.

DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENT

The water or fluid stream treatment process of the present inventioncombines two separate technologies to remove dissolved material andparticulates in a single treatment process. Schematics of this processare shown in FIGS. 1, 2, and 3. The invention will in part be describedbelow as a method of treating drinking water, but the method isapplicable to any suitable fluid stream. With reference to FIG. 1, rawwater from raw water tank 6 is introduced to a process tank 14 underforce of gravity or a pump 7. An adsorbent ion-exchange resin from aresin storage container 10 is added via gravity force or a pumpingsystem 11 to the process tank 14 which contains a submerged membranefilter 12. A suitable submerged filter is the ZEEWEED® membrane (ZENONEnvironmental, Inc., Ontario, Canada). The ion-exchange resin removesdissolved material from the water and the membrane filter removesparticulates. The tank 14 is mixed via aeration by an aeration system 13to suspend the ion-exchange resin. Treated water is extracted throughhollow fiber membranes of the membrane filter 12 using applied vacuum(outside/in) from pump 15 applied to the permeate suction header 17, atwhich point the treated water can be disinfected, stored, anddistributed.

Ion-exchange resins have a finite capacity for adsorbing materials. Whenthis capacity has been reached, the resin must be discarded orregenerated. A high concentration of ion-exchange resin builds up in theprocess tank 14 during the treatment process and can be removed viagravity, or a pump 16. The used ion-exchange resin is then conveyed tothe resin separator 18, where it is extracted from the residual water.The ion-exchange resin may then be regenerated in a regenerationreservoir 20. Typically, regeneration is accomplished by treatment witha high concentration salt solution. Regenerated resin may be returned tothe process tank 14 by a return pump 22 via line 23A or conveyed toresin storage container 10 via line 23B.

In a preferred embodiment, the ion-exchange resin is a magneticion-exchange resin, such as MIEX® DOC manufactured by Orica Watercare,Melbourne, Australia. Preferably, about 20 mL MIEX® DOC resin per literof water is used. In this case, the resin may optionally be removed fromthe membrane filter tank by using a magnetic separator 23 (shown only inFIGS. 2 and 3, but which could also be part of the system shown inFIG. 1) which separates the magnetic resin from the water and othernon-magnetic particles in the tank.

Referring to FIG. 2, in a further embodiment, regeneration of the resinis accomplished in a column 24 where a salt solution is pumped throughthe column to remove material from the resin. The regenerated resin isremoved from the column and can be placed back into the process tank vialine 30. Regenerant waste is disposed through line 32.

Referring to FIG. 3, in another embodiment, the membrane filter cell isisolated, regenerant is added, and mixed with air from air mixing system13 for regeneration. At this point the solution in the tank is removedand passed through the magnetic separator 23 to a resin storage tank 34.

In all cases, regenerated resin is returned to the membrane tankinfluent and the waste regenerant water is disposed of appropriately.

Because the ion-exchange resin of a preferred embodiment is magnetic, ittends to clump together and settle in the process tank 14. To overcomethis tendency, an air-mixing system 13 keeps the magnetic ion-exchangeresin in suspension. This air-mixing system allows for significantlyhigher concentrations of resin in the process tank.

In order to further optimize the system, a mathematical model expressedas a mass balance on resin was developed to determine retention time andion exchange resin concentration in the process tank using the ZEEWEED®membrane and MIEX® DOC resin. For comparison purposes, a basic treatmentprocess using only MIEX® DOC resin and no membrane was also modeled(hereinafter “basic process”). The values applied for the basic processare shown in Table 1, the model values are shown in Table 2, and aschematic shown in FIG. 4. The basic process 40 includes a process orcontact tank 42 to which raw water is added through conduit 44 and anion-exchange resin is added from a resin feed 46. The resin feed 46receives virgin resin from a virgin resin supply 48 and regeneratedresin from a regenerator 50. A gravity separator 52 is provided toseparate ion-exchange resin from the raw water following suitableretention in the process tank, with treated water being output throughconduit 54. Separated ion-exchange resin is conveyed through conduit 56to the regenerator 50 and regenerated resin is delivered to the resinfeed through conduit 58.

The amount of treated water, TW, per day, 1 million gallons, or3,785,000 liters, is the same as the amount of raw water, RW, into thesystem, and water out of the tank, OF. The separator underflow, SU, isthe amount of water leaving the separator, and is the outflow from thetank times the resin concentration, less the amount taking into accountresin loss, given a 30% concentration of resin (volumetric basis), orSU=(OF*RC−OF*RC*RL)/0.3. The resin sent to regeneration, RG, is theamount of outflow times the resin concentration times the amount percentunderflow to regeneration, less the amount for resin loss, orRG=OF*RC*U−OF*RC*U*RL. Recycled resin, RR, goes from the separator backto the contact tank and is the outflow times the resin concentrationless the amount for resin loss, less the amount sent to regeneration, orRR=OF*RC−OF*RC*RL−RG. The amount of regenerated resin that goes backinto the resin feed is equal to the amount of recycled resin. Freshresin fed into the tank is a combination of virgin resin and regeneratedresin. Fresh resin, FR, corresponds to the amount of resin that must beadded to compensate for the amount of resin in stages other than theprocess tank, or FR=OF*RC−RR. Virgin resin, VR, corresponds to the totalamount of resin that must be added to compensate for resin loss, orVR=OF*RL.

Resin Contact Time at Regeneration, CT_(R), is the concentrate timesresin concentration, taking into account the resin loss and the tounderflow sent to regeneration or RC_(R)=RI/[OF*RC−OF*RC*(1−RL)*U].Resin Inventory in Contact Tank, RI, is amount of treated water in thecontact tank times the contact time, CT, times the resin retention time,or RI=RW*CT*RT. Bed Volumes Treated at Regeneration, BV, is the resincontact time at regeneration times the amount of raw water divided bythe resin inventory in the contact tank, or BV=RC_(R)*RW/RI. ResinRetention Time, RT, is the resin inventory in the contact tank dividedby the product of the outflow, resin loss, and resin concentration, orRT=RI/(OF*RL*RC). TABLE 1 Values used in model of basic process.Variable Designation Value Contactor Resin RC 6 mL/L ConcentrationContact Time CT 30 minutes % Underflow to U 10% Regeneration Resin Lossat RL 0.10% Separator Process Flow OF, RW, TW 1 million gallons/day

TABLE 2 Model of basic process. Resin Daily Resin@ Flow Concentration100% Flow Stream L/day % v/v L/day 1 Raw Water 3,785,000 0 0 2 ResinFeed 2,291 100 2,291 3 Contact Tank Outflow 3,785,000 0.60 22,710 4Separator Underflow 75,624 30 22,687 5 Treated Water 3,785,000 0.0006 236 Resin to Regen 2,269 100 2,269 7 Recycle Resin 20,419 100 20,419 8Regenerated Resin 20,419 100 20,419 9 Virgin Resin 23 100 23

The model using the values in Table 3 was applied to the process of thepresent invention using a membrane and magnetic ion-exchange resin(hereinafter membrane/resin process). The model values are shown inTable 4, and a schematic is shown FIG. 5. Briefly, schematic 5Aillustrates a membrane process tank 62 including a membrane filter 63.Raw water enters the membrane process tank through conduit 64 where itis mixed with resin from resin feed 66. Water drawn through the membranefilter 63 exits as treated water at conduit 68. An ion-exchangeresin/raw water mixture is drawn from the membrane process tank throughconduit 70 to resin separator 72. Waste water is removed at conduit 74for suitable disposal. The separated resin is conveyed through conduit76 to the regenerator 78 for regeneration. Regenerated resin is conveyedthrough conduit 80 to the resin feed 66 where it may be mixed orsupplemented with virgin resin from the virgin resin supply 82.

The model is based on a treated water flow TW of 1 million gallons perday or 3,785,000 L/day. Concentrate flows from the process tank to theresin separator. Concentrate is defined as the amount the treated watertimes the amount lost through the membrane recovery, MR, or,C=TW*(1−MR). Raw water into the tank is 3,785,000 L/day plus the amountof concentrate C that is recycled. Treated concentrate, TC is removedfrom the system and is the amount of resin lost from the concentrate, orTC=C*RC*RL. Separator underflow is the water leaving the resinseparator. Separator underflow SU is the concentrate sent to the resinseparator times the resin concentration, taking into account the amountof resin lost, and given a 30% volume/volume concentration of resin, orSU=[C*RC*(1−RL)]/0.3. The separator underflow is split into two parts,the resin to regeneration, RG, and the resin recycled to the processtank, RR. RG is the resin in the concentrate, accounting for resin lossand the underflow sent to regeneration, U, or RG=C*RC*(1−RL)*U. Recycledresin RR is the separator underflow less the resin to regeneration, orRR=C*RC*(1−RL)−(C*RC*U)]−RG. Regenerated resin sent to resin feed is thesame as resin to regeneration, RG. Fresh resin fed into the tank is acombination of virgin resin and regenerated resin. Fresh resin, FR,corresponds to the amount of resin that must be added to compensate forthe amount of resin in stages other than the process tank, orFR=C*RC−RR. The amount of virgin resin in, VR, corresponds to the totalamount of resin in stages of the process other than the process tankless the amount regenerated resin, or VR=FR−RG. Resin Contact Time atRegeneration, C_(TR), is the resin inventory in the contact tank dividedby concentrate times resin concentration, taking into account the resinloss and the underflow sent to regeneration orR_(CR)=RI/[C*RC*(1−RL)*U]. Resin Inventory in Contact Tank, RI, isamount of raw water in the contact tank times the contact time, CT,times the resin retention time, or RI=RW*CT*RT. Bed Volumes Treated atRegeneration, BV, is the resin contact time at regeneration times theamount of treated water divided by the resin inventory in the contacttank, or BV=CT_(R)*TW/RI. Resin Retention Time, RT, is the resininventory in the contact tank divided by the treated concentrate, orRT=RI/TC. TABLE 3 Values used in membrane/resin process. VariableDesignation Value Process Tank Resin RC 25 mL/L Concentration ContactTime CT 12 min. % underflow to U 40% regeneration Resin Loss RL 0.10%Membrane Process MR 95% Recovery Treated Water Flow TW 1 milliongallons/day

TABLE 4 Model of membrane/resin process. Resin Daily Resin @ FlowConcentration 100% Flow Stream (L/day) (% v/v) (L/day) 1 Raw Water3,974,250 0 0 2 Resin Feed 1,895 100 1,895 3 Concentrate 189,250 2.54,731 4 Separator Underflow 15,755 30 4,727 5 Treated Water 3,785,000 00 6 Resin to Regen 1,891 100 1,891 7 Recycle Resin 2,836 100 2,836 8Regenerated Resin 1,891 100 1,891 9 Virgin Resin 5 100 5 10 TreatedConcentrate 5 100 5

A comparison of the results of the two processes in Table 5 indicatesthe improvements of the process of the present invention. TABLE 5Comparison of results from basic and membrane/resin process. Membrane/Basic Resin Variable Designation Process Process Resin Contact Time atCT_(R) 5 10.5 Regeneration (hrs) Bed Volumes Treated at BV 1,668 2,002Regeneration Resin Inventory in Contact RI 473 828 Tank (L) ResinRetention Time (days) RT 21 175 Fresh Resin Dose (mL/L) FR 0.61 0.50Virgin Resin Dose (mL/L) VR 0.0060 0.0012

The resin contact time at Regeneration is increased from 5 hrs to 10.5hrs. The number of bed volumes treated at the regeneration step is alsoincreased from 1,668 to 2,002. The resin inventory in contact tank isgreatly increased from 473 L to 828 L. Because the design of the systemallows the resin to be recycled multiple times, the contact time for theresin will be significantly higher than the hydraulic residence time,HRT-the amount of time that water being treated resides in the treatmentsystem. Resin retention time is also greatly increased from 21 days to175 days. At the same time, the amount of fresh resin dose is decreasedfrom 0.61 mL/L to 0.50 mL/L, and the amount of virgin resin dose is alsodecreased from 0.0060 mL/L to 0.0012 mL/L.

The outputs of the membrane/resin process model, when inputs are varied,are also depicted in FIGS. 6A, 6B, and 6C. FIG. 6A shows the effect ofcontrolling the contactor resin concentration on the bed volumes treatedat regeneration. FIG. 6B is a graph showing the effect of controllingthe contactor HRT on the resin contact time at regeneration. FIG. 6C isa graph showing the effect of controlling resin recycle on the bedvolumes treated at regeneration.

FIG. 7 is a schematic representation of a fluid treatment system 88which incorporates additional features which allow the efficientregeneration of the fluid treatment resin and efficient cleaning of themembrane 12. With reference to FIG. 7, a raw fluid which may be rawwater enters a process tank 14 through fluid inlet 90 and inlet valve91. A mixture of fresh and/or regenerated ion exchange resin or otheradsorbent is added to the raw fluid in the process tank 14 through resininput line 92. The resin or adsorbent is added from a resin storage tank94 by an eductor 96 operating using a source of make up water 98. Theresin/adsorbent is supplied to the eductor 96 at a rate measured with aflow meter 102 and controlled by an isolation valve 104.

During the fluid treatment process, the process tank 14 is aerated froman aeration system 13 using diffused air bubbled through a diffuser 109at the bottom of the process tank 14 to keep the resin/adsorbentsuspended.

A membrane filter 12 driven by a filtrate pump 15 extracts treated fluidfrom the process tank 14. Treated fluid from this step can bedisinfected and, if the fluid is water, used for drinking or otherpurposes. If the fluid is not drinking water, the fluid can be used inan industrial process. When employed with any fluid, the membrane 12filters particles from the fluid and the resin adsorbent removesdissolved material. Although not shown in FIG. 7, a number of processtanks 14 can be operated in parallel for continuous production oftreated fluid during a regeneration, cleaning, and maintenance cycle asdescribed below.

When treatment has progressed to the point where the ion exchange resinor adsorbent reaches its capacity for removal, regeneration may beaccomplished efficiently as follows. The process tank inlet valve 91 isclosed, stopping the input of raw fluid to the process tank 14. Aerationfrom the aeration system 13 through the diffuser 109 is stopped.Cessation of aeration allows the resin in the process tank 14 to settleto the bottom of the process tank 14. After suspended resin has settled,water above the settled resin is removed through the decant line 112through a 3-way valve 114 to the process drain 116. The remaining wateris removed through a strainer 120 and strainer line 122 by opening astrainer valve 124. Preferably, the strainer 120 has sieve openingssized to retain the resin, but allow water and particulate matterrejected by the membrane filter 12 to pass to the process drain 116.After draining, the strainer valve 124 is closed. The resin retained bythe strainer 120 remains in the process tank 14 for regeneration.Regenerant solution, which typically is a concentrated brine solution,is directed from a regenerant solution supply 126 into the process tank14. Air from the aeration supply 13 can be used to mix the resin withthe regenerant. Upon completion of the regeneration process, thestrainer valve 124 is opened, and used regenerant is discharged throughthe strainer line 122 to the process drain 116. Thereupon, rinse waterfrom a rinse water supply 128 enters the process tank 14 for rinsingpurposes. Air from the aeration supply 13 can be used to mix regeneratedresin with rinse water. Upon completion of the rinsing process, thestrainer valve 124 is opened and waste rinse water is discharged to theprocess drain 116. Regenerated resin retained by the strainer 120 willremain in the process tank 14 for use in subsequent fluid treatmentcycles.

Although a substantial portion of the resin will remain in the processtank 14 for use in subsequent treatment cycles, some resin will breakdown or otherwise be lost to the system. Make up resin can be suppliedto the system 88 from the resin storage tank 94. The resin storage tank94 combines regenerated resin withdrawn from the process tank 14 withfresh resin from a fresh resin supply 132 to make up for resin lost tothe system. Make up resin can then be added to the process tank 14through the eductor 96. A fluid treatment cycle subsequent toregeneration and cleaning commences when the eductor 96 water flow isstarted to induce additional resin to the raw fluid supply and the inletvalve 91 is opened.

Periodically, the membrane filter 12 must be cleaned. The watertreatment apparatus 88 provides for cleaning of the membrane filter 12in place. The membrane cleaning process is commenced by closing theprocess tank inlet valve 91. This stops the production of filteredfluid. In addition, aeration from the aeration supply 13 is stopped. Theresin is allowed to settle in the process tank 14. Water above thesettled resin is removed through the decant line 112 through a 3-wayvalve 114 to the process drain 116. Water remaining after decanting isremoved through the strainer 120 and strainer line 122 by opening thestrainer valve 124. After draining, the strainer valve 124 is closed.Resin is removed from the process tank 14 by opening the 3-way resinvalve 118 and directing the resin to the resin storage tank 94 throughthe resin line 130. Next, cleaning solution from a cleaning solutionsupply 134 is directed to the process tank 14. Air from the aerationsupply 13 can be used to better contact the cleaning solution with themembrane 12. After sufficient contact time has expired for the cleaningof the membrane 12, the waste cleaning solution is drained from theprocess tank 14 through the resin line 117 and resin valve 118 anddirected to the process drain 116. Upon draining of the cleaningsolution, the resin valve 118 is closed and rinse water from the rinsewater supply 128 enters the process tank 14. Again, air can be used tobetter contact rinse water with the membrane 12. Waste rinse water exitsthe process tank 14 through the resin line 117 and the resin valve 118.Waste water is ultimately directed to the process drain 116.

The fluid treatment apparatus 88 is particularly well suited to a batchprocessing system where an individual process tank 14 is either engagedin fluid treatment, resin regeneration, or a membrane cleaning step. Theuse of multiple processing tanks 14 connected to the fluid supply inparallel will allow for continuous fluid production.

Additional apparatus can be added to the fluid treatment apparatus 88 toaccomplish the additional steps of regenerant recycling and the recoveryof spent regenerant for use in future generations. A regenerantrecycling and recovery apparatus 140 is shown schematically in FIG. 8.The regenerant recycling and recovery apparatus 140 is an embodimentwhich can be employed as an alternative to draining used regenerantthrough the process drain 116 and out of the system.

The regenerant is typically a strong brine solution which is stored in aregenerant supply 126. Regenerant may be recycled from a regenerationstep in the process tank 14 to the regenerant supply 126 several timesover several regeneration steps without losing its effectiveness.Periodically, however, the regenerant will become contaminated to thepoint where it no longer effectively regenerates spent ion exchangeresin. Spent regenerant can be recovered in a regenerantrecycling/recovery apparatus 140 which preferably features a microscreenpre-filtration module 142 which removes larger particulate contaminantsassociated with the regenerant followed by a nanofiltration membrane 144which removes smaller particulate and dissolved contaminants associatedwith the spent regenerant. Other filtration methods may be employed.Recovered regenerant may then be returned to the regenerant supply 126resulting in significantly less material waste and more efficientoperation.

The fluid treatment, regeneration, membrane cleaning, and regenerantrecycling and recovery steps described above are typically performed asbatch processes. An alternative embodiment shown schematically in FIG. 9includes the use of magnetic ion exchange resin and a magnetic separator23 which allows the fluid treatment system to be run continuously. Inthe embodiment depicted in FIG. 9, magnetic resin is extracted from theprocess tank 14 continuously by a magnetic separator 23. The removedmagnetic resin is passed to a regeneration reservoir 20 whereregeneration takes place. Preferably, the brine or other regenerant usedto accomplish regeneration is recycled from the regenerant storage 126to the regeneration reservoir 20 on a continuous basis. Periodically,the regenerant will become contaminated to such a degree that it is nolonger useful for ion exchange resin regeneration. As shown in FIG. 9,the spent regenerant may be recovered by passing the spent regenerantthrough a microscreen filtration unit 142 to remove larger particles ofcontaminant associated with the regenerant followed by passing theregenerant through a nanofiltration membrane 144 to remove smallerparticulate or dissolved contaminants associated with the regenerant.Thereafter, the regenerant can be returned to the regenerant storage 126for reuse in the continuous system.

The embodiments of Applicant's invention described in detail above arebased upon processes where the ion exchange resin is associated with andintimately contacted with the fluid being treated by means of aerationbased mixing. Alternatively, as shown in FIG. 10, the fluid beingtreated may be contacted with the ion exchange resin by means of anupflow bed 150. The upflow bed can consist of a separate compartment orcompartments in the process tank 14 where ion exchange resin is placedand contained. Fluid to be treated is fed into the process tank 14 atthe inlet 152 which is located at the bottom of the upflow bed 150.Fluid being treated flows upward through the resin until the fluidemerges from an outlet 154 which is located at or near the top of theupflow bed 150. As shown in FIG. 10, the upflow filter bed can be aseparate chamber or chambers defined by a divider or dividers 156 in theprocess tank 14. Multiple ion exchange resin chambers around a singlemembrane tank provides more continuous operation because one ionexchange chamber can be regenerated while the other chambers aretreating raw water. As shown in FIG. 11, the upflow bed can be adiscrete chamber 158. In either embodiment, an aeration supply 13 istypically provided in the process tank under the membrane filter 12 toaid with periodic cleaning of the membrane filter 12.

While the invention has been particularly shown and described withreference to a number of embodiments, it would be understood by thoseskilled in the art that changes in the form and details may be made tothe various embodiments disclosed herein without departing from thespirit and scope of the invention and that the various embodimentsdisclosed herein are not intended to act as limitations on the scope ofthe claims.

1. A method for treating a fluid comprising: a) providing an up-flow bedcontaining an ion-exchange resin within a portion of a process tank; b)removing dissolved contaminants from the fluid by flowing a stream ofthe fluid through the up-flow bed; c) removing particulate contaminantsfrom the fluid by removing treated fluid from the process tank through amembrane filter, wherein said process tank contains said membranefilter; and d) regenerating the ion-exchange resin in the up-flow bedportion of the process tank.
 2. The method of claim 1 further comprisingreusing a regenerant in multiple regeneration steps.
 3. The method ofclaim 2 further comprising filtering the regenerant to restore itsregenerative properties.
 4. A method for treating a fluid comprising: a)providing an up-flow bed containing an ion-exchange resin with an outletof the up-flow bed being in fluid communication with a process tank; b)removing dissolved contaminants from the fluid by flowing the fluidthrough the up-flow bed, out of the outlet and into the process tank; c)removing particulate contaminants from the fluid by passing the up-flowbed treated fluid through a membrane filter, wherein said process tankcontains said membrane filter; and d) regenerating the ion-exchangeresin in the up-flow bed.
 5. The method of claim 4 further comprisingreusing a regenerant in multiple regeneration steps.
 6. The method ofclaim 5 further comprising filtering the regenerant to restore itsregenerative properties.